The Winkler Measurement of Dissolved in Water SCIENTIFIC BIO Introduction FAX! The Winkler method is the standard technique for the determination of dissolved oxygen in fresh and salt water. This scaled-down procedure requires reduced sample volume, reduced reagent volumes, less expense, and less time.

Concepts • Dissolved oxygen • Water quality • Biological oxygen demand • Winkler titration

Materials

Sodium thiosulfate solution, Na2S2O35H2O, 0.0025 M Rubber stoppers, No. 2

Sulfuric acid, H2SO4, 18 M (concentrated) Starch powder, soluble Winkler solution #1 (manganous sulfate) Syringe, 10-mL Winkler solution #2 (alkaline-iodide) Test tube rack Erlenmeyer flask, 125-mL Test tubes, 20 × 150 mm Pipets, Beral-type, thin-stem *Quantities will depend on the number of samples to betested. Review the procedure to determine your requirements.

Safety Precautions This activity requires the use of hazardous components and/or has the potential for hazardous reactions. is extremely cor- rosive to eyes, skin and other tissue. Winkler solution #2 contains sodium hydroxide and sodium iodide, and is also severely corrosive and strongly alkaline. Wear chemical splash goggles, chemical-resistant gloves, and a chemical-resistant apron. Please review current Safety Data Sheets for additional safety, handling, and disposal information.

Preparation Prepare the starch and solutions within a day of use. Refrigerate until use. To make the starch solution, combine 5 g of starch (soluble, potato) with a few milliliters of distilled or deionized water and mix to a uniform paste. Add boiling water up to 100 mL. Stir and continue to heat until starch is completely dissolved. Prepare the sodium thiosulfate solution by dissolving 0.62 g of Na2S2O35H2O (grind the large crystals in a mortar to facilitate weighing) in approximately 500 mL of boiled and cooled distilled or deionized water in a 1000-mL volumetric flask. Dilute up to the 1000 mL mark with additional preboiled water. This solution is perishable, and light and temperature sensitive.

Procedure 1. Collect water samples to be tested in the 20 × 150 mm test tubes. Fill the tubes completely, holding the tube horizon- tally and gently lowering it through the water surface. Stopper the tubes—some water will be displaced—taking care to minimize entrapment of air bubbles. Proceed immediately to step 2. 2. With a Beral-type pipet, add 6 drops of Winkler solution #1 (manganous sulfate solution) directly to the sample tube, holding the pipet tip as close to the sample surface as possible. With a second pipet, add 6 drops of Winkler solution #2 (alkaline-iodide solution) in the same fashion. Stopper the tube and invert several times to mix. This step fixes, or sequesters, the dissolved oxygen in the sample. Fixed samples can be held up to 48 hours before proceeding. 3. Allow the precipitate formed in step 2 to settle to at least one half the volume of the tube (approximately 10–15 minutes).

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4. Add 6–7 drops of concentrated sulfuric acid to each sample tube, stopper and invert several times to mix (the instructor may wish to perform this step). The acid solubilizes the precipitate, giving a clear, yellow-gold solution. 5. With the 25-mL graduated cylinder, transfer 20 mL from the sample tube into a 125-mL Erlenmeyer flask. (Use top solu- tion only—not the bottom with precipitate.) 6. Fill the 10-mL syringe with the sodium thiosulfate solution and note the starting volume. Titrate the sample in the flask with the sodium thiosulfate solution in the syringe until the sample fades to a pale straw color. 7. Add 6 drops of starch solution to the flask and swirl to mix. The sample will turn dark purple-blue. Continue titrating with the sodium thiosulfate solution to the colorless endpoint. 8. Record the total number of milliliters of sodium thiosulfate dispensed from the syringe. This value is directly proportional to the amount of oxygen dissolved in the original sample. Milliliters (mL) of sodium thiosulfate used equals dissolved oxy- gen concentration in milligrams per liter (mg/L); also equivalent to parts per million (ppm).

Disposal Please consult your current Flinn Scientific Catalog/Reference Manual for general guidelines and specific procedures, and review all federal, state and local regulations that may apply, before proceeding. Tested samples, and any unused starch and sodium thiosulfate solutions, can be disposed of by rinsing down the drain with excess water according to Flinn Suggested Disposal Method #26b.

Connecting to the National Standards This laboratory activity relates to the following National Science Education Standards (1996): Unifying Concepts and Processes: Grades K–12 Evidence, models, and explanation Constancy, change, and measurement Content Standards: Grades 5–8 Content Standard A: Science as Inquiry Content Standard B: Physical Science, properties and changes of properties in matter Content Standard C: Life Science, structure and function in living systems, populations and ecosystems Content Standards: Grades 9–12 Content Standard A: Science as Inquiry Content Standard B: Physical Science, chemical reactions Content Standard C: Life Science, interdependence of organisms; matter, energy, and organization in living systems Content Standard F: Science in Personal and Social Perspectives, natural resources, environmental quality, natural and human-induced hazards

Discussion The relevant chemical reactions occurring throughout the procedure are outlined below: 2+ – Mn + 2OH + 1/2 O2  oxygen- complex + H2O (1) + – 2+ oxygen-manganese complex + 4H + 2I  I2 + Mn + 2H2O (2)

I2 + 2Na2S2O3  Na2S4O6 + 2NaI (3) Addition of the manganous sulfate and the alkaline-iodide results in the formation of an insoluble oxygen-manganese complex (1), the precipitate in step 2. The oxygen is stable in this form for several days. Both the manganous sulfate and the alkaline- iodide are added in excess to ensure reaction with all of the oxygen. Treatment with the sulfuric acid dissolves the complex and liberates free iodine (2), imparting the distinctive yellow-gold color. The amount of free iodine is proportional to the amount of oxygen dissolved in the original sample. By titrating a measured portion of the sample against a standardized sodium thiosul- fate solution (3), the amount of free iodine—and the corresponding amount of oxygen—is determined. The starch “indicator” (which forms a distinctly colored complex with the free iodine) is used to provide an unmistakable visual endpoint for the titration.

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The concentration of dissolved oxygen (DO) is one of the most important indicators of the overall health of a body of water. Waters with consistently high levels of DO (> 6 mg/L) typically support the most diverse biological communities. Waters with consistently low DO levels (< 3 mg/L) may be virtually devoid of aquatic life or may harbor only a few species adapted to such conditions.

References Bunce, N. J. Environmental Chemistry; Wuerz: Winnipeg, Canada, 1991; pp 118–120. Mitchell, M. K.; Stapp, W. B. Field Manual for Water Quality Monitoring; 9th ed.; Thomson-Shore: Dexter, Michigan, 1995; pp 27–33.

Materials for The Winkler Titration are available from Flinn Scientific, Inc. Catalog No. Description W0010 (W0005) Winkler Solution #1, 100 mL, 500 mL W0011 (W0006) Winkler Solution #2, 100 mL, 500 mL S0122 Starch, Potato, Soluble, 100 g S0114 Sodium Thiosulfate, Crystal, 500 g S0143 Sulfuric Acid, 18 M, 473 mL Consult the Flinn Scientific website for current prices.

3 © 2017 Flinn Scientific, Inc. All Rights Reserved.